OBJECTIVES To investigate the relation between levels of cumulative exposure to wood dust and respiratory symptoms and the occurrence of bronchial hyperresponsiveness among beech and oak workers.
METHODS 114 Male woodworkers from five furniture factories and 13 male unexposed controls were examined. The unexposed control group was supplemented by 200 male historical controls. Statistical analyses were performed excluding and including the historical controls. Dust concentration was measured by personal sampling methods. Cumulative exposure to dust was calculated for each woodworker by multiplying the duration of the work by the intensity of exposure (years.mg/m3). Bronchial hyperresponsiveness was assessed by the methacholine bronchial challenge test. Subjects were labelled methacholine bronchial challenge positive if forced expiratory volume in 1 second (FEV1) fell by ⩾20%. The linear dose-response slope was calculated as the last dose divided by the total dose given.
RESULTS 443 Dust samples were collected. The median cumulative exposure to dust was 110 years.mg/m3 with lower and upper quartiles at 70 and 160 years.mg/m3 Overall, no declines in FEV1 and forced vital capacity (FVC) were found with increasing exposures. A dose-response relation was found between intensity of exposure on the one hand, and sore throat, increased prevalence of positive methacholine bronchial challenge tests, and steeper dose-response slope, on the other.
CONCLUSION Exposure to oak and beech dust may lead to the development of sore throat and bronchial hyperresponsiveness.
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The association between occupational exposure to wood dust and asthma has long been known.1 Among the various species of wood identified as being linked to asthma,2 western red cedar (Thuja plicata)3-14 has been extensively studied. In a pair of benchmark papers, Chan-Yeunget al 5-7 described the clinical pictures and natural history of cedar asthma, identified plicatic acid as the chemical compound in the dust responsible for the asthmatic reaction, and showed that only half the workers who leave a job because of cedar asthma become asymptomatic, whereas the remaining half continue to experience recurrent attacks of asthma.
Exposure to wood dust can cause adverse respiratory effects which are independent of asthma. In 1982, Chan-Yeung et al 8 carried out an epidemiological study of sawmill cedar workers and compared the findings with those of office workers not exposed to respiratory pollutants. They found that cedar workers had significantly higher prevalence of chronic respiratory symptoms and lower lung function compared with office workers. These persisted even after asthmatic workers (wheezers) were excluded from the analysis. Subsequent examinations, carried out over an 11 year time span, showed that sawmill cedar workers had significantly greater decline in forced expiratory volume in 1 second (FEV1) and forced vital capacity (FVC) than office workers and that a dose-response relation existed between the intensity of exposure and the annual decline in FVC.14
In woodworkers, the development of either variable or fixed airflow obstruction depends on predisposing host factors and environmental factors, especially the nature and intensity of exposure to dust. In 1995, we started a longitudinal survey of bronchial hyperresponsiveness in furniture workers exposed to beech and oak dust, a matter on which there is virtually no information in the epidemiological literature. Our purpose was to examine the possible relation between symptoms and bronchial hyperresponsiveness and intensity of chronic exposure measured objectively. In this report we present the results from the initial (cross sectional) survey.
Subjects and methods
The study we report on was a cross sectional survey of male employees, comprising the workforce at five wooden furniture factories processing mainly beech (Fagus sp) and oak (Quercus sp). The factories were situated in eastern France, within a radius of 40 km from the city of Neufchateau. Except for salesmen, all current male woodworkers were invited to participate in the study: 135 (92.7% of the workforce) accepted this invitation. Excluded from the study were those subjects who had never been exposed to wood dust but only to vapours or dust from varnish (n=7). An additional group of 14 subjects was also excluded because (a) they were unable to perform pulmonary function tests correctly, (b) because of a history of previous exposure to substances known to induce bronchial hyperresponsiveness—for example, flour dust—and (c) they had experienced a possible past exposure to wood dust or varnish which could not be assessed adequately. This left a total of 114 exposed workers. As our aim was to examine the occurrence of pulmonary abnormalities as a function of exposure, a homogeneous split of the sample across the observed range of exposure was planned. The control population from nearby factories was a group of 13 unexposed male workers of similar socioeconomic status, who were examined in the course of the study; they were supplemented by 200 male historical controls, the data for whom had been collected by our team in the years 1991–3 for former studies.15 The socioeconomic status of the historical controls was similar to that of workers in the present study; they represented 95% of the workforce at pollution free workshops of the following industries: glass making 1 (n=48); glass making 2 (n=24); glass making 3 (n=19); electrical engineering (n=6); caterers (n=9); food distribution (n=27); stationery (n=27); and salt packing (n=40). Moreover, they were examined according to a protocol identical to that used in this study including pulmonary function and methacholine challenge test, which were carried out by the same experienced technician with the same equipment.
Examinations were carried out between November 1995 and April 1996. Written, informed consent was given by all subjects. Information was obtained on age, working hours a day, working duration, and occupational history. The prestudy characteristics of the study group and historical controls are shown in table 1.
Measurement of concentrations of airborne dust was carried out by an industrial hygienist from our institution (Laboratoire Interrégional de Chimie de l'Est) on several occasions from 1986 to 1995. During each survey, a work site inspection was conducted which included assessments of the types and layout of woodworking machinery, local exhaust ventilation, and wood use. Closed face filter holders (Millipore, MA, USA) housing preweighed 37 mm diameter glass microfibre filters (GF/C, Whitman) were used. The cassettes were connected to portable, battery operated sampling pumps, sampling at flow rates of 1 l.min-1. The average inhalable particulate concentration mg/m3 was measured from the increased filter mass (Mettler M3 microbalance) and rates and duration of airflow. Care was taken to avoid the collection of “inertials”—that is large particles propelled from high speed machines during sampling.
Detailed histories of respiratory diseases and smoking habits were recorded in a two part questionnaire The first was a modified version of the European Coal and Steel Community questionnaire on respiratory symptoms16 which was given by an experienced physician. Chronic bronchitis was defined as cough and phlegm for at least 3 months each year for not less than 2 successive years. The term chronic cough and/or phlegm was used to define subjects complaining of chronic cough or phlegm regardless of duration: thus, it encompassed both those subjects who fulfilled the criteria for chronic bronchitis and those who did not. Bouts of bronchitis was the term coined to define those subjects who answered yes to the question: “Have you ever experienced an increase in the severity of cough and in the volume of sputum production of at least 3 weeks duration during the past 3 years?”. Dyspnoea on exertion was considered to be present when the subjects complained of breathlessness while walking up a slight hill. Adult asthma was defined as asthma which has been diagnosed by a physician at age ⩾16.
The second part of the questionnaire asked for acute irritant symptoms that the subjects attributed directly to their work. They were considered to be present when the subject answered affirmatively to the questions: “Have you ever had complaints at work of red (burning) (weary) eyes ?”; “Have you ever had complaints at work of a runny (burning) nose ?”; “Have you ever had complaints at work of a sore throat?”; and “Have you ever had complaints at work of a dry (irritant) cough?”. A positive answer to these questions should be followed to a positive answer to the question: “Do these complaints disappear when you leave work (evenings, weekends, holidays)?”
Non-smokers were defined as subjects who had never regularly smoked ⩾1 cigarette a day or had smoked ⩾1 cigarette a day for <1 year. Current smokers were defined as subjects who reported regular smoking of ⩾1 cigarette a day for ⩾1 year. Ex-smokers were subjects who reported smoking ⩾1 cigarette regularly in the past but who had stopped smoking at least 1 year before the study.
Pulmonary function tests
Spirometry was carried out by the same experienced technician (JPT), with an electronic spirometer (Spiro-Analyzer ST 300, Fukuda Sangyo, Tokyo, Japan). The following indices were obtained by the subject expiring forcefully and maximally after a maximal inspiratory manoeuvre: FVC, FEV1, and maximal expiratory flows at various lung volumes. At baseline each subject performed ⩾3 reproducible forced expiratory manoeuvres (within 5% for FVC and FEV1); thereafter only two reproducible curves were required. The curve with the highest sum of FVC+FEV1 was used for statistical analysis. The results were expressed as the difference between the observed and predicted values of the European Respiratory Society.17
As the examinations were carried out during workshifts, an abbreviated version of the methacholine bronchial challenge test was used.18 The technique has been described previously.19 20 Two different dose schedules were outlined for subjects with either slightly abnormal lung function or normal lung function, respectively. After baseline spirometry the subject inhaled an aerosol of normal saline, then spirometry was repeated. In subjects whose baseline spirometry was normal and whose FEV1 fell by <10% after the inhalation of normal saline, three cumulative doses of methacholine (0.5, 2.5, and 7.5 μmol) were given with an inhaler (Mediprom FDC 88 - Paris, France) delivering doses of 0.5 μmol of methacholine per breath. The system is equipped with a nebuliser (De Vilbiss 5610 D) delivering particles 3 μm in diameter. A noseclip was worn and the aerosol inhaled through the mouth slowly. Then the breath was held for 5 seconds. Spirometry was performed in the sitting position, before and 3 minutes after the inhalations of methacholine. The challenge test was discontinued either after the inhalation of the third dose of methacholine or if the FEV1 fell by ⩾20% below the baseline value. Subjects whose FEV1/FVC was ⩽80%, baseline FEV1⩽70%, and whose FEV1 fell by <10% after saline, were given an initial dose of methacholine of only 10 μg (0.05 μmol).
Subjects who experienced a fall in FEV1 of ⩾20% were classified as having a positive methacholine bronchial challenge test. As it could be anticipated that many subjects would fail to experience this specific response, an additional non-censored index of responsiveness was calculated—namely, the linear two point dose-response slope as proposed by O'Connor et al.21 The dose-response slope was calculated as the ratio of the percentage fall in FEV1 at the last dose: the total dose of methacholine (μmol) given.
The study was approved by the local medical ethics committee.
Statistical analysis was carried out with the SAS statistical software.22 Multiple logistic regression analyses were used to assess the effect of the exposure on the symptoms and the presence of a positive methacholine bronchial challenge test while adjusting for the possible confounding factors, especially smoking. Multiple linear regression was used to describe the effect of exposure on the baseline spirometric variables (controlling for smoking), and on the transformed dose-response slope adjusted on baseline FEV1 and age. The transformation we used (1/(% fall FEV1/μmol+2.5)) was applied to normalise its statistical distribution in view of multiple regression analyses. This transformation was found to be optimal for a large unexposed population.19 Thus, a value of 0.25 corresponds to a fall in FEV1 of 1.5% per μmol of methacholine, whereas a value of 0.30 corresponds to a fall in FEV1 of 0.8% per μmol of methacholine. The stability of the variance and approximate linearities in the linear models were checked on residual plots.
To show possible quantitative trends with increasing cumulative exposure to dust, the raw data are displayed in six exposure groups: historical controls, controls collected in the course of the present data collection with no exposure and four groups labelled of equal size and increasing cumulative exposure to dust. However, all trends in the regression analyses were fitted as linear continuous cumulative exposure to dust and thus independent of this grouping.
Two series of statistical analyses were performed excluding and including historical controls. The analyses incorporating historical controls were done in the context of so called mixed models with the PROC MIXED program.22 These analyses acknowledge that there may be a between study heterogeneity which is explicitly taken into account as a between population variance. Details and a discussion of this statistical model in this context are presented in a recent paper.15
A total of 443 personal time weighted average (TWA) samples were collected between 1986 and 1996 in 28 similar wooden furniture factories (including three of those in this study) located in the same area, and using the same types of wood. A detailed analysis of these exposure data by machine showed that: (a) sanding operations were consistently associated with higher exposure levels; (b) exhaust ventilation resulted in roughly dividing the exposure data by two; (c) all other tasks resulted in roughly comparable exposure intensities; and (d) no systematic differences between factories resulted after taking into account sanding and exhaust ventilation (table 2). On the basis of these measurements, each job was assigned an estimated dust exposure based on the mean value of all dust measurements for that job. Thus, an estimated dust exposure of 13 mg/m3 was assigned to all workers performing sanding operations in areas without local exhaust ventilation whereas an estimated dust exposure of 8 mg/m3was assigned to those in areas with local exhaust ventilation. For the remaining tasks, workers in areas with and without local exhaust ventilation were assigned estimated dust exposures of respectively 4 and 6 mg/m3 whatever the job classification. To assess lifetime exposures the cumulative exposure index was calculated for each woodworker by multiplying the years of work with the assigned exposure intensity (years.mg/m3). For workers who had worked in various workstations the total cumulative exposure was obtained by summing up the cumulative exposure corresponding to each workstation.
The median cumulative exposure to dust was found at 110 years.mg/m3—that is, 11 years at a 10 mg/m3exposure intensity. Of the exposed population 25% (n=28) had a cumulative exposure to dust <71 years.mg/m3; whereas 33 subjects (33%) had a cumulative exposure to dust >162 years.mg/m3 which corresponds to about 12 years of sanding without exhaust ventilation.
RESPIRATORY AND IRRITANT SYMPTOMS
The prevalence of symptoms as a function of the cumulative exposure is shown in table 3. Overall, the prevalence of chronic respiratory symptoms tended to be low, ranging from 0% for chronic bronchitis (group with 70–110 years.mg/m3), bouts of bronchitis (groups with 0 and 70–110 years.mg/m3), asthma (group 0 years.mg/m3) and dyspnoea (group 0 years.mg/m3) to 12% for chronic cough or phlegm (groups with 110–160 and >160 years.mg/m3). The prevalence of irritant symptoms tended to be somewhat higher than that of chronic symptoms with maximal values of 32% for red (burning) eyes in the group with 70–110 years.mg/m3. However, only the prevalence of sore throat increased significantly with increasing exposure, a finding compatible with a dose-response relation.
BASELINE LEVEL OF PULMONARY FUNCTION
Table 4 shows the pulmonary function variables of historical controls and woodworkers according to the various classes of cumulative exposure. Overall, the measured values tended to exceed the predicted ones for most variables. In the exposed group the observed excess FVC ranged from 202 to 280 ml. As FEV1 tended to increase proportionally more markedly than FVC, the observed FEV1/FVC ratio was slightly greater than the predicted one. For maximal expiratory flows, a pattern of high flows at mid-lung volume (Vemax50) and low flows at low lung volume (Vemax25) was observed: Vemax50 exceeded the predicted one by an amount ranging from 37 (with 0 exposure) to 561 ml/s (with 0–70 years.mg/m3). For Vemax25, the observed value tended to be generally lower than the predicted one: the observed difference ranged from −230 (with 0 exposure) to −382 ml/s (with <160 years.mg/m3). In the group with 0–70 years.mg/m3, the observed values of Vemax25 slightly exceeded the predicted one. Finally, it is important to notice that no overall relation was found between the respiratory flows (or any other lung function variable) and the cumulative exposure index.
The results of the methacholine bronchial challenge test in historical controls and exposed workers are shown in table 5. Overall, a significant relation was found between the two indices of bronchial responsiveness and intensity of exposure. Both the proportion of subjects with a positive methacholine bronchial challenge test (a fall in FEV1 ⩾20%) and the steepness of the dose-response slope increased significantly with increasing cumulative exposures, a finding compatible with a dose-response relation.
The adverse respiratory effects of exposure to wood dust vary according to the wood species.23 Although cases of asthma have been described on exposure to oak dust, both this wood and beech are better known for their carcinogenic effects.23 In this investigation, we found that occupational exposure to beech and oak dust is associated with non-malignant respiratory illness.
In the present study, the furniture workers underwent a heavy exposure to dust. The measured dust concentrations—which ranged from 2.96 to 8.34 mg/m3 for operations with exhaust ventilation and from 4.37 to 12.74 mg/m3 for those without exhaust ventilation—largely exceeded the 2.5 mg/m3 permissible concentration (for western red cedar dust) in British Columbia,14 and the threshold limit value (time weighted average) of 1 mg/m3 adopted in France,24 the threshold limit value of 1 mg/m3 for hardwood proposed by the American Conference of Governmental Industry,25 or the health based limit of 0.2 mg/m3 recommended by the Dutch Expert Committee for Occupational Standards (DECOS).26
This is the only study in which the association between levels of bronchial responsiveness and measured exposure in oak and beech workers has been evaluated. There are only a few epidemiological studies dealing with bronchial responsiveness and exposure in unselected woodworkers. Chan-Yeung et al 8examined a large sample of cedar mill workers (n=652) and office workers (n=440) and found a higher prevalence of bronchial hyperresponsiveness among cedar workers which increased with the duration of employment compared with the office workers. Subsequently, Vedal et al 11 followed up a subsample (n=227) of the same group of cedar workers who had had bronchial challenge testing performed on at least two occasions over a 2 year period. They found that subjects with persistent bronchial hyperresponsiveness had higher initial estimated exposure to total airborne dust than did office workers. Dahlqvist et al 27 evaluated the bronchial responsiveness to methacholine of woodtrimmers (n=28) at a Swedish sawmill and unexposed office workers (n=19). The rate of positive response was greater in the woodtrimmers (29% v 10%) but the difference was not significant probably due to the small sample size. Finally, more recently, Malmberg et al 28 reported the results of a cross sectional survey of bronchial responsiveness and pulmonary function tests in Swedish sawmill workers (n=169) exposed to Scots pine and Norway spruce. They found the airways of the exposed workers (workers inside the sawing area; n=59) to be more responsive than the airways of unexposed workers (workers outside the sawing area; n=39). Together with our study, and despite differences in methodology, these studies give support to the idea that a relation exists between bronchial hyperresponsiveness and exposure to wood dust.
The present study showed that the levels of bronchial responsiveness of beech and oak workers increased significantly with increasing intensities of exposure, a finding not paralleled by a similar increase in the prevalence of symptoms of asthma nor a decline in indices of airway patency. One way to explain this set of findings is to invoke selection by the healthy worker effect. The implication is that beech and oak workers with bronchial hyperresponsiveness who develop disabling symptoms or lung function abnormalities related to exposure tend to move to less exposed places or to leave the job altogether, leaving the place to those with varying degrees of responsiveness but few or no symptoms. However, this is only conjecture because of the cross sectional nature of this (initial) survey.
Alternatively, it could be postulated that beech and oak are wood species which contain relatively low concentrations of sensitisers so they would cause increased responsiveness mainly through mechanical irritation. The increased prevalence of sore throat with increasing intensities of exposure is compatible with this explanation. However, the reported association between exposure to either oak29 30 or beech31 dust and episodes of bronchial asthma suggests that workers may become sensitised as well. Data on the irritant, toxic, and sensitising wood species of commercial value show that oak is rich in catechols, which are the most potent sensitisers from natural sources, whereas beech contains, besides other compounds, sesquiterpene lactones with both sensitising and irritant properties.31
The relation between exposure to wood dust and bronchial hyperresponsiveness was examined by deriving a cumulative exposure index in the standard way with quantitative exposure estimates of industry specific job exposure matrices. Such an index was for instance used in a recent study of lifeguards exposed to nitrogen trichloride.32 In the present study, the index assumes that the mean dust concentrations found when machining in many factories are representative of the concentrations found when machining in our furniture factories. This assumption is supported by dust measurements carried out by our team over several years (P Gouet, unpublished observations) which showed that, for a given process and working conditions, the dust concentrations linked to two similar machines in two different factories were comparable with one another. Giving further support to this assumption is the fact that the pattern of exposure in this study is similar to that reported for other furniture factories.33
Notwithstanding these considerations, we think that the possibility of misclassification cannot be ruled out entirely. However, a non-differential (random) misclassification would usually weaken the chance of finding an association existing between exposure and effect. It is therefore unlikely that the association found is due to an exposure misclassification. On the contrary, it is more likely that the necessarily imperfect historical assessment of exposure has led to an underestimation of the exposure-response association found.
A last limitation of our study is its relatively small size, so that we were only able to show relations between respiratory health and exposure to wood dust because the exposure was relatively high. Our study sheds no light on the possible effects of low exposure on respiratory health, for which larger sample sizes are necessary.
Finally, it should be stressed that the dose-response relations we found cannot be attributed to the inclusion of the historical controls as similar results were found when the analysis was done with only the small group of non-exposed controls.
In conclusion, in woodworkers exposed to beech and oak dust the risk of developing a sore throat because of bronchial responsiveness after inhaling methacholine increases with increasing exposure intensities. Hopefully our longitudinal follow up of these workers will help us to better understand the relevance of these findings.
We thank the woodworkers for their participation and the management staff members of the factories and the occupational physicians for their invaluable help in conducting this study.
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